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Latest GHG Inventory shows California remains below 2020 emissions target; much steeper rate of GHG reductions required

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tons per person to 10.7 tons per person in 2018, a 24% decrease. in 2018 (2000-2018 average year-over-year increase is 6.8%), continuing the increasing trend as they replace Ozone Depleting Substances (ODS) being phased out under the 1987 Montreal Protocol. Emissions from high-GWP gases increased 2.3% Source: CARB GHG Inventory.

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PSI team develops web tool for consumers to compare environmental impact of passenger cars in detail

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The system will graph lifecycle impact for a range of specified powertrains, for a large number of impact categories: Climate change [kg CO 2 -eq.]. Deterioration of the ozone layer [kg CFC-11-eq.]. Noise emissions [Person-Pascal/second]. Depletion of fossil energy resources [kg oil-eq.]. Human toxicity [kg 1,4-DC-eq.].

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German-Chilean consortium investigating new ways of reducing arsenic in copper concentrates: ReAK

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However, climate change has caused an increase in rainfall in recent years, which now raises the issue of environmental contamination. Other project partners are also evaluating UV- and ozone-assisted as well as microbial oxidation processes. These calcium compounds are then deposited in the Atacama Desert.

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Up close and personal with Volkswagen’s e-Golf carbon offset project: Garcia River Forest

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ozone depletion potential (ODP). photochemical ozone creation potential. REDD+ is a specific implementation of a climate change mitigation solution of the UN-REDD Programme. Click to enlarge. acidification potential. global warming potential for a reference period of 100 years (GWP).

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What is the Electric Vehicle Approved (EVA) Scheme?

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Global warming plays a role in thinning the ozone layer, thus permitting harmful rays’ penetration to the earth. Address climate emergency- the climate is changing rapidly. This organisation is responsible for addressing climatic changes and how to cope with them.

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Study finds climate impact of long distance trip can vary by factor of 10 depending upon mode, efficiency and occupancy

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compared the specific climate impact of long-distance car travel with bus, train, or air trips. They accounted for both CO 2 emissions and emissions of ozone precursors (NO x , VOC, CO) and aerosols (BC or black carbon, OC, SO 2 ) as well as cloud effects (aviation-induced cirrus clouds and contrails)—i.e.,

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